The Arizona Toad (Bufo [ = Anaxyrus] microscaphus) occupied the entire Agua Fria River drainage in central Arizona until relatively recently. By the 1980s, a close relative, Woodhouse's Toad (Bufo woodhousii), colonized the lower reaches of the Agua Fria and replaced B. microscaphus at some sites. We tested the hypothesis that habitat disturbance drives replacement of B. microscaphus by B. woodhousii, via hybridization, by examining shifts in the distribution of these toads following the expansion of the Waddell Dam on the lower Agua Fria River in the early 1990s. As of 2010, the high elevation headwaters of the Agua Fria River were still occupied by B. microscaphus, the lower reaches near the confluence with the Gila River were occupied by B. woodhousii, and along the middle reaches, hybridization between these two anurans occurred at the same three sites as documented in the early 1990s. Contrary to expectations, evidence of hybridization along middle reaches of the river is largely unchanged: B. microscaphus has not been replaced by B. woodhousii at any additional sites nor is there any evidence of introgression of woodhousii mtDNA into putatively “pure” microscaphus populations upstream of hybrid sites.

The ecological consequences of impoundment construction on riparian systems throughout the U.S. Southwest has profoundly affected a variety of organisms, including many amphibians. To better understand the current extent of hybridization and changes in genetic composition over time in Bufo (Anaxyrus) woodhousii and Bufo microscaphus, we used microsatellite loci to evaluate 260 individuals representing 10 total populations constituting B. woodhousii, B. microscaphus, and putative hybrids along the Agua Fria River in Arizona during two time periods (1992–97 and 2009–10). Consistent with prior work with these two anurans documenting unidirectional replacement or genetic introgression, we predicted that microsatellites would provide evidence of directional introgression of B. woodhousii into B. microscaphus. The putative hybrid populations exhibited the highest number of alleles, and B. microscaphus exhibited the lowest number of alleles. Structure analysis indicated K = 2 as the best-fit population number for both time periods. All pairwise F-statistics were highly significant, corroborating differentiation among populations as inferred by structure analysis. The principal coordinates analysis demonstrated three distinct clusters of individuals that corresponded strongly with prior morphological and mitochondrial assignments within this region over both sampling periods. Our findings indicate that the genetic identity of B. microscaphus remains distinct from B. woodhousii and the hybrids, suggesting that the genetic structure of the corresponding populations has remained intact. Bufo woodhousii has not replaced B. microscaphus along the Agua Fria River beyond those habitats directly associated with impoundment construction.

We tried to correlate the level of genetic introgression in native brown trout populations with some physicochemical and environmental features. Introgresión rates were calculated according the presence (assessed by PCR-RFLP as described by Mc Meel et al. 2001) of the LDH C1*90 allele in the populations, which is fixed in central European populations used for restocking, whereas LDH C1*100 is the fixed allele in wild Mediterranean populations in the area of study. Water quality variables were obtained from Confederación Hidrográfica del Ebro data in 10-year series before sampling. Physicochemical characteristics as conductivity, pH, bicarbonates, temperature and Oxygen saturation were analyzed. Average, minimum and maximum, standard deviation and coefficient of variation were calculated for each of the above parameters. Populations were classified as wild (0% introgresión), low affected (less than 10% individuals), highly affected (10-50%) and severely affected (more than 50%). We found that highly affected populations are generally associated to higher minimum temperature and pH as well as to wide oscillations in oxygen saturation levels. Success in restocking using stocks of Atlantic domestic trout is strongly influenced by environmental features. Fortunately, wild populations show a better adaptation being able to colonise the most adverse environments. Restocking policies should be fully revised to preserve wild trout populations.

We tried to correlate the level of genetic introgression in native brown trout populations with some physicochemical and environmental features. Introgresión rates were calculated according the presence (assessed by PCR-RFLP as described by Mc Meel et al. 2001) of the LDH C1*90 allele in the populations, which is fixed in central European populations used for restocking, whereas LDH C1*100 is the fixed allele in wild Mediterranean populations in the area of study. Water quality variables were obtained from Confederación Hidrográfica del Ebro data in 10-year series before sampling. Physicochemical characteristics as conductivity, pH, bicarbonates, temperature and Oxygen saturation were analyzed. Average, minimum and maximum, standard deviation and coefficient of variation were calculated for each of the above parameters. Populations were classified as wild (0% introgresión), low affected (less than 10% individuals), highly affected (10-50%) and severely affected (more than 50%). We found that highly affected populations are generally associated to higher minimum temperature and pH as well as to wide oscillations in oxygen saturation levels. Success in restocking using stocks of Atlantic domestic trout is strongly influenced by environmental features. Fortunately, wild populations show a better adaptation being able to colonise the most adverse environments. Restocking policies should be fully revised to preserve wild trout populations